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Dynamics versus optimization in non-convex environmental economics problems with a single welfare function
Ashwin K. Seshadri and Shoibal Chakravarty
Economics has a well-defined notion of equilibrium. Unlike mechanics or thermodynamics, economics does not include explicit theories of dynamics describing how equilibria are reached or whether they are stable.
However, even simple economics problems such as maximization of a welfare function might sometimes be interpreted as dynamics problems. Here we consider when dynamics is relevant to welfare optimization problems involving a single decision-maker, for example, a social decision-maker maximizing a social wel- fare function. We suggest that dynamics occurs in case a welfare maximum can only be known through a se- quence of local computations. These local computations give rise to a dynamical system, and the welfare optimum is also equilibrium. On the contrary, if the welfare function is known, then dynamics is irrelevant and the maximum can be chosen directly. The importance of choosing the right metaphor for an economics problem is discussed.
A common problem in climate change economics is determining the optimal level of mitigation1, maximizing econo- mic benefits of mitigation for the entire world, defined as the difference between benefits and costs2. In the absence of un- certainty, this would correspond to some level of global warming. Such welfare optima are conceptually different from equilibria in economics. A well-known introductory economics textbook de- scribes equilibrium as a ‘state in which an economic entity is at rest or in which the forces operating on the entity are in balance so that there is no tendency for change’3. However, the notion of equilib- rium in economics also derives from mathematical optima, though this is usu- ally elided4.
Generally, however, these notions are different. If T* degrees of global warm- ing is believed to be the welfare maxi- mizing solution, then policymakers might consider how to arrange, for ex- ample, through price or quantity instru- ments, that T* were reached by the economic system. Whatever T were actually reached would be the result of equilibria in the relevant markets for emissions generating activities, and in that sense T could be called the equilib- rium level of warming. Even if T and T*
were to coincide, the welfare optimum and policy equilibrium would only con- tingently be the same.
The parallels that equilibrium thinking in economics has with physics are not only semantic. Neoclassical economics was inspired by physics, with economic equilibrium discussed as a balance bet- ween gradients of utilities, in analogy
with force balance in mechanics5,6. How- ever, unlike in mechanics, economic theory did not include description of processes leading to equilibrium. Sub- sequently efforts were made in econo- mics to revise the analogy to equilibrium thermodynamics, to distinguish micro- scopic from macroscopic variables6, but the basic difficulty remained. Economics omits dynamics of how equilibria are at- tained; imagine equilibrium thermody- namics without a kinetic theory of gases.
Moreover, this feature of economics has advantages, avoiding messy explanations that would have had to include psychol- ogy, sociology, etc. which are difficult to represent. However, economic equilib- rium invokes the same concept of equi- librium as physical theory, but without the scaffolding of dynamics.
For example, a price on CO2 emissions would raise the supply curve of CO2
emitting activities (i.e. make their supply more expensive), thereby reducing the equilibrium quantity of emissions. How- ever, for reaching an equilibrium either or both sides of the relevant eco- nomic exchanges must gather informa- tion about the shape of supply and demand and estimate the equilibrium, either in a single step or as an iterative process, with the latter giving rise to a dynamical system. Economics does not make such an iterative process explicit.
A unique intersection between demand and supply curves occurs in case the functions describing the utility of con- sumption and the cost of production are convex. This guarantees that their deriva- tives, the demand and supply curves, are monotonic with unique intersection3,7.
Such thinking underlying convex prob- lems played a role in the marginalist approach to economics, involving com- parison between marginal quantities (de- rivatives of costs, benefits, etc.), to reach an optimum7,8.
In case of a single welfare function, the welfare optimizing solution can be treated as equating two marginal quanti- ties, for example, that of a benefit and a cost. However, such balancing using algebra to identify the maximum does not turn such welfare maxima into equi- libria, because equilibrium implies also that the agents involved have no ten- dency to change their behaviour to move them away from the equilibrium.
What then is the relation between these notions? We propose that a welfare maximum is also equilibrium when there is dynamics involved, for instance, when reached iteratively. Then a dynamics metaphor pertains to the problem, be- cause the maximum is only reached iteratively, through repeated local computations; a sequence of iterative
‘calculate–act–calculate–act–...’ steps progressively leads to the maximum.
The ‘calculate’ step determines the subsequent ‘act’ step; for example, a firm might use estimates of marginal cost and marginal revenue in the neighbour- hood of the present output to estimate a change in output in the next period that increases profit. Such calculation must be only approximate because these graphs are not known; otherwise, the maximum could be selected in a single step. Furthermore, each ‘act’ step creates conditions for a new ‘calculate’ step, and this information could not be learned in
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any other way. This is similar to a dyna- mical system taking small steps on a tra- jectory along a local gradient. This iterative process will lead to the optimal solution in a convex economics problem.
Applying the dynamics metaphor to economics problems implies that direct optimization is impossible. If the welfare function were already known, the maxi- mum could be arrived at directly instead of relying on a slow iterative process.
The dynamics metaphor treats the eco- nomics actor as a gradient-following particle, with only local knowledge in a small neighbourhood of any choice made. This is a stronger assumption than utility maximization, entailing not only consistent preferences but also limited information that precludes making (glob- ally) optimizing decisions in a single step. Implications are sharpest in non- convex economics problems where the two metaphors, dynamics and optimiza- tion, can yield different results.
With non-convexity there can be mul- tiple stationary points of the welfare
function9, corresponding to multiple intersections between marginal curves being compared. Multiple local maxima can create difficulties for analysis.
Pigou10 in an early discussion of a non- convex situation in economics, writes ‘in any industry where the conditions are such that there is not only one, but more than one, volume of investment which would yield a marginal social net product equal in value to that obtainable else- where, unless it so happens that the vol- ume actually hit upon is that one of these which is the most favourable to the national dividend, an opening for im- provement must exist. Benefit could be secured by a temporary bounty (or tem- porary protection) so arranged as to jerk the industrial system out of its present poise at a position of relative maximum, and induce it to settle down again at the position of absolute maximum’10. Pigou’s metaphor is of dynamics with multiple stable equilibria, where the decision-maker for the firm (think of the CEO or plant manager) cannot choose
the absolute maximum directly, because that is not known, as information is only local. The firm may have to be nudged using policy so that it can eventually progress from its local maximum to attain the absolute maximum. Such prob- lems are objects for a dynamics meta- phor. The corresponding optima are also equilibria, because they are reached through an approximate dynamical proc- ess and only persist if stable. Further- more, they are objects for policy if either the system could settle into a local maxi- mum that is worse than the global maxi- mum, or if policymakers have a different view of social welfare, for example, be- cause they have a longer time-horizon.
How about choosing the optimal level of mitigation that maximizes a welfare function, the difference between benefits and costs of mitigation at various degrees of global warming? In this context, it has been pointed out11 that impacts for some sectors of the economy might be non- convex. Therefore, contradictory to the conventional case of diminishing bene- fits to mitigation at lower levels of warming, there might be an intermediate temperature range where the benefits of mitigation are more sensitive to global warming. This can lead to multiple inter- sections of the marginal benefits and costs graphs, and hence multiple local maxima of the welfare function. There- fore, the authors raise the possibility of
‘policy tipping’ from a low-warming, high-cost, low-impact regime to a high- warming, low-cost, high-impact regime11. Figure 1 illustrates such a non-convex problem.
Here is an example where the entire welfare function is known, and the wel- fare optimum need not be attained by an iterative process. The best solution among the current possibilities can be chosen directly, and there is no dynamics involved (Figure 1b)12. Therefore, there is no dynamical process ensuring stabil- ity of the chosen solution either, and the question of tendency for change cannot arise. In this problem, local optima of the welfare function are not economic equi- libria despite corresponding to a balance between marginal costs and benefits of mitigation.
Returning to the general situation, we noted previously that an iterative process is relevant when only local information is available. In such cases the chosen welfare optima might be termed equilib- ria. This is despite the fact that economic Figure 1. Illustration of a hypothetical non-convex climate change economics prob-
lem11. a, Marginal benefits and costs as a function of warming. The marginal benefits function is not monotonic, since the benefits curve is non-convex. b, W elfare function indicating global maximum A and local maximum B. If the welfare function is known, the global maximum A can be chosen directly.
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theory generally does not make dynamics explicit, since the welfare optimum can only be reached by some unspecified dynamical process in such a situation.
The second condition for dynamics to apply is that each step in the process helps generate additional information for approaching the welfare optimum. From this, we deduce that the iterative process only applies where feedback from action to information occurs rapidly. Therefore, among such cases the relevant question is: is information only local? If the entire welfare function is known, then the cor- rect metaphor is that of optimization, dynamics is not relevant, and the welfare optimum is not equilibrium. When faced with a non-convex economics problem, it is important to recognize the correct meta- phor, which affects both the language employed to describe that problem as well as conclusions reached from analysis.
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2. Weitzmann, M. L., Rev. Econ. Stud., 1974, 41, 477–491.
3. Samuelson, P. A. and Nordhaus, W. D., Economics 19e, McGraw-Hill, New York, 2010.
4. Tieben, B. The Concept of Equilibrium in Different Economic Traditions: An Historical Investigation, Edward Elgar, 2012.
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Economics as Social Physics, Physics as Nature’s Economics, Cambridge Univer- sity Press, Cambridge, UK, 1991.
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Control, 2008, 32, 7–65.
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8. Aspromourgos, T., Cambridge J. Econ., 1986, 10, 265–270.
9. Mas-Colell, A., In The New Palgrave: A Dictionary of Economics (eds Eatwell, J., Milgate, M. and Newman, P.), Palgrave Macmillan, London, 1987.
10. Pigou, A. C., The Economics of Welfare, Macmillan, London, 1920.
11. Ricke, K. L., Moreno-Cruz, J. B., Schewe, J., Levermann, A. and Caldeira, K., Nature Geosci., 2016, 9, 5–6.
12. As the authors furthermore discuss, fail- ure to mitigate emissions rapidly could render what was previously the global optimum solution unreachable, due to physical and economic constraints. In re- considering the policy goal the starting position would then be irreversibly dif- ferent, presenting a new problem, and the original problem would then be improp- erly posed. This merely reflects the diffi- culty of simplifying a time-dependent dynamic optimization problem to the very different static one of choosing a single quantity, the maximum global warming.
Ashwin K. Seshadri* is in the Divecha Centre for Climate Change, Indian Insti- tute of Science, Bengaluru 560 012, India; Shoibal Chakravarty is in the School of Natural Sciences and Engi- neering, National Institute of Advanced Studies, Bengaluru 560 012, India.
*e-mail: [email protected]
OPINION
Weedomics a need of time
Niraj Tripathi
Weeds are the plants, found simultane- ously with crops and out-compete them in more or less every aspect. Competitive characters and tolerance to various abiotic and biotic stresses are the signifi- cant qualities which can be identified amongst a variety of weed species and can be transferred into crop plants for their advancement. Plant molecular biol- ogy includes the study of cellular proc- esses, their genetic management and links with alterations in their adjoining.
Advancement and accessibility of the so- phisticated molecular tools offers us lib- erty to play with different metabolic pathways at molecular level and to trans- fer the desirable genetic materials into crop plants, thus breaking the reproduc- tive barriers for interspecific and inter- generic transfer of the genetic material.
Advanced plant molecular biology tools offer fabulous promises for elucidating these imperative traits from weed species in detail and further exploration for the
diverse aspects of crop improvement in future. The large scale studies connecting entire genetic, structural, or functional machinery are called ‘omics’. Major segments of omics consist of genomics, transcriptomics, proteomics, metallom- ics, metabolomics, ionomics and phe- nomics. At present these advances are frequently used in crop improvement.
However, success of such approaches re- quires joint efforts from scientists to work mutually with expertise in weed science, molecular breeding and plant physiology. So the combined omic ap- proaches in weed species (weedomics) for crop improvement may play a sig- nificant role in changing climatic condi- tions for food security (Figure 1).
Genomic helps in clarification of taxo- nomy and evolutionary relationships, uncover evidence of closely related species that cannot be morphologically distinguished (cryptic species) and hybridization events, elucidate methods
of reproduction, determine population structure and origins of target weeds.
These may help in biological control of invasive weeds. Advances in weed geno- mics can contribute to crop improvement by better understanding of the biological mechanisms and improved screening methods for selecting superior genotypes more efficiently which possess novel genes to provide resistance against adverse climatic conditions and biotic stresses. A wide range of defense mechanisms are activated that increases plant tolerance against adverse condi- tions to avoid damage imposed by stresses. The first step toward stress response is stress signal recognition and subsequent molecular, biochemical and physiological responses activated through signal transduction1. Under- standing such responses is important for effective management of stress. Weeds possess higher level of stress tolerance and their transcriptome profiling may